Explained — All Silva

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Arboricultural consultancy explained — for homeowners, architects, and developers who want to understand what they're being asked for and why.

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Reports & surveys

A BS 5837 tree survey is the foundation of almost every arboricultural instruction in the UK. Before any design work can meaningfully engage with trees on or near a development site, you need to know what's there — the species, size, condition, and crucially, the retention value of each tree.

The survey is carried out by a qualified arboriculturist who visits the site, assesses every relevant tree, and records the findings in a Schedule of Trees. Each tree is assigned a category:

Category A

High quality. Significant amenity value. Must be given maximum protection.

Category B

Moderate quality. Notable amenity value. Should be retained where possible.

Category C

Low quality or limited life expectancy. Retention desirable but less critical.

Category U

Unsuitable for retention. Recommended for removal regardless of development.

The survey data feeds every other document — the AIA, TCP, TPP, and AMS. Without it, nothing else can be properly prepared, and the Local Planning Authority will not determine a tree-related application.

When you need this
  • Before submitting any planning application involving trees
  • At the earliest design stage — ideally before architects draw anything
  • When purchasing land and needing to understand tree constraints
  • When a planning condition references a tree schedule

A Tree Constraints Plan is a scaled drawing — typically overlaid onto an OS base or topographic survey — that shows the Root Protection Areas, canopy spreads, and physical constraints posed by the trees on and adjacent to your site.

Think of it as a spatial translation of the survey data. It tells architects and designers where they can and cannot build before any scheme is committed to. A good TCP produced early can save significant abortive design costs.

The TCP is a drawing, not a report. It accompanies — rather than replaces — the written survey schedule. Most planning applications require both.

When you need this
  • At the design briefing stage, to inform the architect's layout
  • As part of a pre-application enquiry to the LPA
  • With any full planning application where trees are present

The AIA is the principal technical report submitted with a planning application where development will affect trees. It takes the survey data and asks a structured question: what will this development do to these trees, and is that impact acceptable?

It evaluates the design against the tree constraints, quantifies any losses by category, and sets out the arboricultural justification for the scheme as proposed. Where trees are to be removed, it must demonstrate that the loss is necessary and proportionate.

A well-prepared AIA is the document that makes or breaks planning consent where trees are concerned. A generic approach will draw queries and conditions; a precise one closes the conversation before it opens.

When you need this
  • With any planning application where development affects trees
  • Where the site contains TPO'd trees or is within a Conservation Area
  • Where trees are to be removed or their root zones encroached upon
  • When an LPA pre-application response has flagged tree concerns
Site context Design appraisal Loss quantification Planning policy review BNG considerations

A Tree Protection Plan is a scaled drawing that specifies how trees will be physically protected on site during construction. It shows the location, type, and extent of protective barriers — usually Heras fencing or timber post-and-rail — along with the Construction Exclusion Zone within which no works, storage, or vehicle movements may take place.

It is a planning condition deliverable. In most cases where an AIA is submitted, a TPP will be required either before determination or as a pre-commencement condition. It must reference the specifications set out in BS 5837:2012 Appendix 4.

When you need this
  • As a planning condition — pre-determination or pre-commencement
  • Whenever construction will take place near retained trees
  • When discharging a planning condition referencing tree protection
  • Before site works begin on any scheme with retained trees

Where the TPP shows where protection will be in place, the AMS explains how the works will be carried out. It is a written specification of the construction methodology in proximity to trees — covering demolition sequence, ground protection, drainage, and foundation design.

An AMS is required whenever work must take place within or close to the Root Protection Area of a retained tree. It gives the Tree Officer technical assurance, and gives the contractor clear, enforceable instructions.

An AMS almost always includes or references a Detailed TPP as a component part — the drawing and written methodology together form the complete protection package submitted as a pre-commencement condition.

Demolition methodology Ground protection spec Foundation design Services installation method Contractor briefing Monitoring provisions

This distinction causes more confusion than almost anything else in BS 5837 practice — and it matters, because submitting the wrong level of detail at the wrong stage can result in a planning condition not being properly discharged.

Outline TPP

Submitted with the planning application. Shows the principle of protection — approximate barrier locations and extent of the exclusion zone. Design may still be evolving.

Detailed TPP

Produced post-consent once the design is fixed. Forms part of the AMS. Must be precise — exact barrier positions, access routes, compound locations, services runs.

Many applications incorrectly submit a detailed TPP at application stage, locking in construction details before the design is complete. Getting the level right for each stage matters — we advise on this as a matter of course.

Even the best TPP and AMS cannot protect trees on their own — they need to be implemented correctly on site. A watching brief involves a qualified arboriculturist attending site at key construction stages to verify that the approved methodology is being followed.

Attendance may be periodic — for specific operations such as protection installation, demolition, or excavation near roots — or continuous where the risk to retained trees is high. A written record of each visit forms the evidence trail required to discharge the relevant planning condition.

When you need this
  • When a planning condition requires arboricultural supervision
  • During any works within or adjacent to an RPA
  • Where TPO'd or high-value trees are at particular risk
  • When the contractor has limited experience working near trees
Root protection

The Root Protection Area is a defined zone around a tree that represents the minimum area required to protect its roots and the soil structure around them. It's not arbitrary — it's a mathematically derived area calculated under BS 5837:2012 to reflect the actual extent of a tree's root system relative to its size.

radius = 12 × DBH Root Protection Area (RPA) — BS 5837:2012 trunk RPA boundary
The RPA is calculated as a circle with radius = 12 × the stem diameter (DBH measured at 1.5m height)
Single stem

Radius = 12 × stem diameter at 1.5m. Result expressed as a circle on plan.

Multi-stem

Combined stem diameter calculated by formula. Reflects total canopy mass.

Maximum cap

For very large or veteran trees, the RPA is capped at 707m² — approximately 15m radius.

You can calculate the RPA for your tree using our free RPA calculator tool →

The default position for most Local Planning Authorities is that no structures, excavations, or materials storage should be located within an RPA. However, if work is genuinely unavoidable, solutions exist — and there are far more of them than most people realise.

The key is providing the Tree Officer with technical certainty: a demonstrable methodology showing how the tree will survive the works. This is delivered through an Arboricultural Method Statement.

Specialist solutions that allow work within an RPA
  • No-dig cellular systems for driveways and car parks
  • Screw-pile and suspended beam foundations that bridge over roots
  • Directional drilling for service runs — gas, water, drainage
  • Permeable paving where hardstanding is unavoidable
  • Air-spading for non-destructive root mapping
  • Root barrier systems to redirect growth without harming the tree
  • "Top-down, pull-back" demolition methodology
  • Impermeable liners to prevent concrete leachate reaching roots

Most people focus on the obvious — a digger hitting a root. The reality is considerably broader, and many of the most damaging actions appear entirely harmless at the time.

Soil compaction

Heavy machinery — and even foot traffic over wet ground — crushes air pockets that roots need to breathe.

Chemical leaching

Cement mixing, fuel spills, and concrete washings alter soil pH to levels that are lethal to roots.

Level changes

Lowering ground by 150mm can sever enough roots to destabilise a tree. Raising levels smothers them.

Severed service runs

New drainage, gas pipes, and telecoms cables are among the most common root severance causes on real sites.

Impermeable hardstanding

Paving within the RPA — even without excavation — cuts off water and gas exchange to the roots.

Shading by new buildings

Sustained shadow cast by a new structure can gradually weaken an established tree over years.

Leaf accumulation

Enclosed courtyards or changed drainage that pools leaf litter against a stem can promote collar rot.

Root dehydration

Deep excavations outside the RPA can act as a drainage sump, drawing moisture away from the root zone.

Tree death rarely happens overnight. Symptoms may not appear for three to five years — by which point there is no remedy. Prevention, not cure.

Construction & site protection

Heras fencing — the familiar mesh panel fencing seen on construction sites — is the standard physical barrier used to create a Construction Exclusion Zone around retained trees. It is specified in BS 5837:2012 as the default protection system because it is visible, robust, and temporary.

The fencing must be erected before any site works begin and must remain in place until practical completion. Nothing — no plant, no materials, no spoil, no site welfare facilities — may be placed within the zone it defines.

RPA boundary (excl. zone) Heras fencing Heras fencing installed at or beyond the RPA boundary before works commence
Heras fencing defines the Construction Exclusion Zone — the no-go area for the duration of the build

Heras fencing must be installed before any plant enters the site — not after. It is not unusual for a watching brief to catch contractors who have moved or removed panels during works. This is a breach of the planning condition and must be reported.

Ground screws (also called screw piles or helical piles) are steel foundation elements that are rotated into the ground rather than driven or cast in concrete. They are one of the most important tools in the arboriculturist's toolkit when construction must occur within or near a Root Protection Area.

The reason they are so valuable for tree protection is simple: they require minimal ground disturbance. A standard strip or pad foundation involves excavation, spoil removal, and concrete poured directly into the ground — all of which cause significant damage to the root zone. A screw pile displaces a fraction of the soil, requires no concrete, and can be positioned with precision to avoid mapped root locations.

How they work

A steel shaft with helical flights is rotated into the ground using a hydraulic torque motor — similar in principle to a corkscrew. The head is then connected to the structure above.

Suspended beam

Screw piles are typically combined with a steel or timber beam that spans between them, lifting the structure clear of the ground and "bridging" over the root zone entirely.

Reversible

Unlike concrete foundations, screw piles can be removed, making them a genuinely low-impact option for temporary or sensitive structures.

They are commonly used for extensions, raised decks, outbuildings, and driveways where conventional foundations would be unacceptable within the RPA. An AMS must specify the pile locations and confirm they have been designed to avoid root conflicts — sometimes informed by prior air-spading to map root distribution.

An air spade is a specialist tool that uses a high-velocity jet of compressed air to break up and displace soil without cutting or damaging roots. It allows an arboriculturist to excavate around a tree's root system and map exactly where the roots are — without causing harm to them in the process.

This matters enormously on complex sites. BS 5837 RPAs are calculated estimates — they tell you roughly where roots are likely to be. Air spading tells you where they actually are, which is often considerably different, especially on urban sites where roots have followed paths of least resistance through disturbed ground.

When air spading is used
  • Before specifying foundation or pile positions within an RPA
  • When root mapping is required to justify a revised exclusion zone
  • To investigate suspected root damage or decay at the base of a tree
  • To improve soil structure around a tree that is declining (decompaction)
  • As part of an AMS to demonstrate precision root avoidance

No-dig cellular systems (sometimes called geocell or cellular confinement systems) are three-dimensional plastic grids that sit on the existing ground surface and are filled with gravel or other permeable material. They provide a loadbearing surface for vehicles without requiring any excavation into the root zone.

They are one of the most commonly specified solutions where a driveway or car park surface must pass through or into an RPA. Because no excavation is required, the root system is left intact, and water and gas can continue to exchange through the fill material.

Simply choosing a permeable surface material — gravel, permeable block paving — is not sufficient if the sub-base installation requires excavation through the root zone. The system specification, not just the surface, must be no-dig.

Planning & law

A Tree Preservation Order is a legal instrument made by a Local Planning Authority that protects specific trees or groups of trees from being cut down, uprooted, or wilfully damaged without prior consent. TPOs are made under the Town and Country Planning (Tree Preservation) (England) Regulations 2012.

A TPO can protect an individual tree, a group of trees, an area, or a woodland. They are attached to the land rather than the owner, so they remain in force even when a property is sold.

What requires prior consent under a TPO
  • Felling or removing the tree
  • Carrying out any pruning works (even minor)
  • Wilful damage — including root damage from construction
  • Any works within the root zone that could harm the tree

Carrying out unauthorised works to a TPO'd tree is a criminal offence carrying an unlimited fine. This applies to the landowner, contractor, and anyone directing the works.

To apply for consent to carry out works to a TPO'd tree, you must submit a Section 211 notice (for Conservation Area trees) or a TPO application to the LPA. An arboricultural report justifying the works is typically required.

Yes. Any tree with a trunk diameter exceeding 75mm at 1.5m height within a designated Conservation Area is protected by default — even without an individual TPO. Before carrying out any pruning, felling, or significant root disturbance, you must give the Local Planning Authority six weeks' written notice (known as a Section 211 notice).

During those six weeks, the LPA can choose to make a TPO if they consider the tree to be of sufficient amenity value. If they do not respond, you may proceed with the works after the notice period expires.

Carrying out works to a Conservation Area tree without giving notice is a criminal offence, carrying the same unlimited fine as unauthorised works to a TPO'd tree.

Exemptions — no notice required for
  • Trees with trunk diameter under 75mm at 1.5m height
  • Dead trees (where death can be demonstrated)
  • Works required to abate a legal nuisance
  • Works required urgently in the interests of safety

Not always — but more often than most applicants expect. The National Planning Policy Framework (NPPF) requires LPAs to ensure that applications affecting trees include sufficient information to assess the impact. In practice, this means a BS 5837 survey is expected whenever:

When a tree survey is likely to be required
  • Any tree on or adjacent to the site could be affected by the works
  • The site contains or is adjacent to TPO'd trees
  • The site is within a Conservation Area
  • The development is within the likely root zone of any significant tree
  • The LPA's validation checklist specifically requests one

For very small extensions where no trees are within the likely influence zone, a survey may not be required. However, submitting without one when trees are present risks the application being invalidated at validation stage, or refused at determination.

If in doubt, commission the survey. The cost of a survey is a fraction of the cost of having an application delayed, invalidated, or refused because the LPA doesn't have the information it needs.

If a tree that was required to be retained under a planning condition dies during or after development, the planning authority can enforce the condition and require replacement planting. Planning conditions that protect trees typically include wording requiring that any retained tree that dies within a defined period (commonly five years post-completion) must be replaced with an equivalent or agreed specimen.

Where the tree was subject to a TPO and dies as a result of construction activity that was not approved, the landowner and/or developer may face enforcement action and prosecution, as well as a requirement to plant a replacement.

Tree decline after construction is often slow and insidious — symptoms appearing years after the damage occurred. This makes attribution difficult but not impossible. A watching brief creates a contemporaneous record of site conditions that can be used in any subsequent investigation.

Ecology & biodiversity

Biodiversity Net Gain is a requirement under the Environment Act 2021 that all new developments in England must deliver a measurable 10% improvement in biodiversity compared to the pre-development baseline. It became mandatory for most planning applications from February 2024.

Trees — and in particular the loss of trees — interact with BNG in a significant and often underappreciated way. Individual trees of significant size and maturity contribute meaningfully to the biodiversity baseline calculation, and their loss must be offset. Retained mature trees, by contrast, can provide a substantial positive contribution to a development's biodiversity metric.

Trees lost

Felling trees — particularly Category A and B specimens — reduces the biodiversity baseline and increases the BNG offset required.

Trees retained

Retaining high-quality trees can contribute positively to BNG and reduce the extent of new habitat creation required elsewhere.

New planting

New tree planting can contribute to BNG, but young trees score far lower than mature specimens — another argument for retention over removal.

The interaction between arboricultural assessment and BNG calculation is an area where early, coordinated input from both disciplines can significantly improve a development's performance — and reduce the mitigation burden. We work alongside ecologists to ensure tree retention strategies support BNG objectives.

Ancient and veteran trees are recognised in the NPPF (2024) as irreplaceable habitats — a designation that places them in the same category as ancient woodland, blanket bog, and limestone pavement. Development that would result in their loss or deterioration will be refused unless there are wholly exceptional reasons.

Ancient tree

A tree in the third and final stage of its life. Defined by characteristics — hollowing, dead wood, reduced crown — rather than age alone. Often millennia old for some species.

Veteran tree

A tree showing veteran characteristics — typically wildlife habitats within the tree itself — but not yet in its ancient phase. Can occur at any age depending on species and conditions.

Ancient and veteran trees are ecologically irreplaceable. They host specialist invertebrates, fungi, lichens, and birds that depend on the specific microhabitats only old trees provide — features that take centuries to develop. No amount of replacement planting can compensate for their loss within any planning timeframe.

If you have an ancient or veteran tree on or near your site
  • Involve an arboriculturist before any design work is undertaken
  • Assume a larger buffer than the standard BS 5837 RPA
  • Expect the LPA to apply significant weight to its retention
  • Consider specialist ecological survey to record its habitat features

Yes — trees with cavities, crevices, loose bark, dense ivy, or large forks can all provide roost habitat for bats. All bat species in the UK are strictly protected under the Wildlife and Countryside Act 1981 and the Conservation of Habitats and Species Regulations 2017. It is a criminal offence to disturb, injure, or kill a bat, or to damage or destroy a roost — whether or not bats are present at the time.

If any trees scheduled for removal or works show features that could support bats, a Preliminary Roost Assessment (PRA) by a licensed ecologist is required before any works can proceed. If the PRA identifies potential roost features, further survey — typically bat activity transects conducted at specific times of year — will be needed before a European Protected Species licence can be obtained.

Felling a bat-roost tree without a licence is a serious criminal offence, regardless of planning permission to do so. Planning permission and ecological licensing are separate processes — both must be in place before works begin.

Trees most likely to support bat roosts
  • Mature trees with cavities or hollow sections
  • Trees with loose or flaking bark
  • Trees covered in dense ivy
  • Veteran or ancient specimens
  • Trees with large forks or wounds that have sealed over

Ancient woodland is land that has been continuously wooded since at least 1600AD. Like ancient trees, it is classified by the NPPF as an irreplaceable habitat. The policy presumption against development that would damage or destroy ancient woodland is extremely strong — refusal is the default position.

The key practical point for development is the buffer zone. Natural England advises a minimum 50-metre buffer between any new development and the boundary of ancient woodland. This buffer is not just about the trees at the edge — it protects the woodland's hydrology, microclimatic conditions, soil ecology, and understorey habitats from the indirect effects of development.

The presence of Ancient Woodland Indicator species — plants such as bluebell, wood anemone, and yellow archangel — in hedgerows or scrub adjacent to a site can indicate that the ground was formerly wooded. This can extend planning protection well beyond any mapped woodland boundary.

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